US6973775B2 - Method for desulfating a nitrogen oxide storage catalyst - Google Patents
Method for desulfating a nitrogen oxide storage catalyst Download PDFInfo
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- US6973775B2 US6973775B2 US10/637,884 US63788403A US6973775B2 US 6973775 B2 US6973775 B2 US 6973775B2 US 63788403 A US63788403 A US 63788403A US 6973775 B2 US6973775 B2 US 6973775B2
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- United States
- Prior art keywords
- storage catalyst
- desulfation
- catalyst
- exhaust gas
- lean
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- MWUXSHHQAYIFBG-UHFFFAOYSA-N Nitric oxide Chemical compound O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 title claims abstract description 250
- 239000003054 catalyst Substances 0.000 title claims abstract description 94
- 238000000034 method Methods 0.000 title claims abstract description 29
- 239000007789 gas Substances 0.000 claims abstract description 38
- 239000000446 fuel Substances 0.000 claims abstract description 34
- 239000000203 mixture Substances 0.000 claims abstract description 22
- 229910052815 sulfur oxide Inorganic materials 0.000 claims abstract description 20
- 238000003795 desorption Methods 0.000 claims abstract description 19
- 238000000746 purification Methods 0.000 claims abstract description 16
- XTQHKBHJIVJGKJ-UHFFFAOYSA-N sulfur monoxide Chemical class S=O XTQHKBHJIVJGKJ-UHFFFAOYSA-N 0.000 claims abstract description 14
- 238000002485 combustion reaction Methods 0.000 claims description 12
- 238000010438 heat treatment Methods 0.000 claims description 8
- 238000002347 injection Methods 0.000 claims description 3
- 239000007924 injection Substances 0.000 claims description 3
- 230000008929 regeneration Effects 0.000 description 20
- 238000011069 regeneration method Methods 0.000 description 20
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 13
- 239000001301 oxygen Substances 0.000 description 13
- 229910052760 oxygen Inorganic materials 0.000 description 13
- RAHZWNYVWXNFOC-UHFFFAOYSA-N Sulphur dioxide Chemical compound O=S=O RAHZWNYVWXNFOC-UHFFFAOYSA-N 0.000 description 8
- RWSOTUBLDIXVET-UHFFFAOYSA-N Dihydrogen sulfide Chemical compound S RWSOTUBLDIXVET-UHFFFAOYSA-N 0.000 description 7
- 229910000037 hydrogen sulfide Inorganic materials 0.000 description 7
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 description 6
- BASFCYQUMIYNBI-UHFFFAOYSA-N platinum Chemical compound [Pt] BASFCYQUMIYNBI-UHFFFAOYSA-N 0.000 description 6
- 229910052717 sulfur Inorganic materials 0.000 description 6
- 239000011593 sulfur Substances 0.000 description 6
- AKEJUJNQAAGONA-UHFFFAOYSA-N sulfur trioxide Chemical compound O=S(=O)=O AKEJUJNQAAGONA-UHFFFAOYSA-N 0.000 description 6
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 4
- JJWKPURADFRFRB-UHFFFAOYSA-N carbonyl sulfide Chemical compound O=C=S JJWKPURADFRFRB-UHFFFAOYSA-N 0.000 description 4
- 239000011232 storage material Substances 0.000 description 4
- 238000011144 upstream manufacturing Methods 0.000 description 4
- 238000010521 absorption reaction Methods 0.000 description 3
- 230000015572 biosynthetic process Effects 0.000 description 3
- 239000000463 material Substances 0.000 description 3
- 238000013178 mathematical model Methods 0.000 description 3
- 150000002823 nitrates Chemical class 0.000 description 3
- 229910052697 platinum Inorganic materials 0.000 description 3
- 238000001179 sorption measurement Methods 0.000 description 3
- 150000003467 sulfuric acid derivatives Chemical class 0.000 description 3
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 description 2
- DGAQECJNVWCQMB-PUAWFVPOSA-M Ilexoside XXIX Chemical compound C[C@@H]1CC[C@@]2(CC[C@@]3(C(=CC[C@H]4[C@]3(CC[C@@H]5[C@@]4(CC[C@@H](C5(C)C)OS(=O)(=O)[O-])C)C)[C@@H]2[C@]1(C)O)C)C(=O)O[C@H]6[C@@H]([C@H]([C@@H]([C@H](O6)CO)O)O)O.[Na+] DGAQECJNVWCQMB-PUAWFVPOSA-M 0.000 description 2
- WHXSMMKQMYFTQS-UHFFFAOYSA-N Lithium Chemical compound [Li] WHXSMMKQMYFTQS-UHFFFAOYSA-N 0.000 description 2
- ZLMJMSJWJFRBEC-UHFFFAOYSA-N Potassium Chemical compound [K] ZLMJMSJWJFRBEC-UHFFFAOYSA-N 0.000 description 2
- 229910052783 alkali metal Inorganic materials 0.000 description 2
- 150000001340 alkali metals Chemical class 0.000 description 2
- 229910052784 alkaline earth metal Inorganic materials 0.000 description 2
- 150000001342 alkaline earth metals Chemical class 0.000 description 2
- 229910052788 barium Inorganic materials 0.000 description 2
- DSAJWYNOEDNPEQ-UHFFFAOYSA-N barium atom Chemical compound [Ba] DSAJWYNOEDNPEQ-UHFFFAOYSA-N 0.000 description 2
- 229910052792 caesium Inorganic materials 0.000 description 2
- TVFDJXOCXUVLDH-UHFFFAOYSA-N caesium atom Chemical compound [Cs] TVFDJXOCXUVLDH-UHFFFAOYSA-N 0.000 description 2
- 229910052791 calcium Inorganic materials 0.000 description 2
- 239000011575 calcium Substances 0.000 description 2
- 229910052746 lanthanum Inorganic materials 0.000 description 2
- FZLIPJUXYLNCLC-UHFFFAOYSA-N lanthanum atom Chemical compound [La] FZLIPJUXYLNCLC-UHFFFAOYSA-N 0.000 description 2
- 229910052744 lithium Inorganic materials 0.000 description 2
- 229910052757 nitrogen Inorganic materials 0.000 description 2
- 231100000572 poisoning Toxicity 0.000 description 2
- 230000000607 poisoning effect Effects 0.000 description 2
- 229910052700 potassium Inorganic materials 0.000 description 2
- 239000011591 potassium Substances 0.000 description 2
- 229910052761 rare earth metal Inorganic materials 0.000 description 2
- 150000002910 rare earth metals Chemical class 0.000 description 2
- 229910052708 sodium Inorganic materials 0.000 description 2
- 239000011734 sodium Substances 0.000 description 2
- 229910052727 yttrium Inorganic materials 0.000 description 2
- VWQVUPCCIRVNHF-UHFFFAOYSA-N yttrium atom Chemical compound [Y] VWQVUPCCIRVNHF-UHFFFAOYSA-N 0.000 description 2
- MGWGWNFMUOTEHG-UHFFFAOYSA-N 4-(3,5-dimethylphenyl)-1,3-thiazol-2-amine Chemical compound CC1=CC(C)=CC(C=2N=C(N)SC=2)=C1 MGWGWNFMUOTEHG-UHFFFAOYSA-N 0.000 description 1
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 1
- 229910052684 Cerium Inorganic materials 0.000 description 1
- FYYHWMGAXLPEAU-UHFFFAOYSA-N Magnesium Chemical compound [Mg] FYYHWMGAXLPEAU-UHFFFAOYSA-N 0.000 description 1
- 206010037660 Pyrexia Diseases 0.000 description 1
- QAOWNCQODCNURD-UHFFFAOYSA-L Sulfate Chemical compound [O-]S([O-])(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-L 0.000 description 1
- 229910002091 carbon monoxide Inorganic materials 0.000 description 1
- ZMIGMASIKSOYAM-UHFFFAOYSA-N cerium Chemical compound [Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce] ZMIGMASIKSOYAM-UHFFFAOYSA-N 0.000 description 1
- 229910000420 cerium oxide Inorganic materials 0.000 description 1
- 239000000567 combustion gas Substances 0.000 description 1
- 150000001875 compounds Chemical class 0.000 description 1
- 238000007796 conventional method Methods 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 238000001514 detection method Methods 0.000 description 1
- 239000002283 diesel fuel Substances 0.000 description 1
- 229930195733 hydrocarbon Natural products 0.000 description 1
- 150000002430 hydrocarbons Chemical class 0.000 description 1
- 239000001257 hydrogen Substances 0.000 description 1
- 229910052739 hydrogen Inorganic materials 0.000 description 1
- 125000004435 hydrogen atom Chemical class [H]* 0.000 description 1
- 238000009434 installation Methods 0.000 description 1
- 238000011068 loading method Methods 0.000 description 1
- 229910052749 magnesium Inorganic materials 0.000 description 1
- 239000011777 magnesium Substances 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- JCXJVPUVTGWSNB-UHFFFAOYSA-N nitrogen dioxide Inorganic materials O=[N]=O JCXJVPUVTGWSNB-UHFFFAOYSA-N 0.000 description 1
- 229910000510 noble metal Inorganic materials 0.000 description 1
- 230000010355 oscillation Effects 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 230000001590 oxidative effect Effects 0.000 description 1
- BMMGVYCKOGBVEV-UHFFFAOYSA-N oxo(oxoceriooxy)cerium Chemical compound [Ce]=O.O=[Ce]=O BMMGVYCKOGBVEV-UHFFFAOYSA-N 0.000 description 1
- 239000002574 poison Substances 0.000 description 1
- 231100000614 poison Toxicity 0.000 description 1
- 230000001902 propagating effect Effects 0.000 description 1
- 230000001105 regulatory effect Effects 0.000 description 1
- 229910052712 strontium Inorganic materials 0.000 description 1
- CIOAGBVUUVVLOB-UHFFFAOYSA-N strontium atom Chemical compound [Sr] CIOAGBVUUVVLOB-UHFFFAOYSA-N 0.000 description 1
- 150000003464 sulfur compounds Chemical class 0.000 description 1
- 230000008646 thermal stress Effects 0.000 description 1
- 231100000331 toxic Toxicity 0.000 description 1
- 230000002588 toxic effect Effects 0.000 description 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Chemical compound O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 1
Classifications
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F01—MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
- F01N—GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL COMBUSTION ENGINES
- F01N3/00—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust
- F01N3/08—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous
- F01N3/10—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by thermal or catalytic conversion of noxious components of exhaust
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/92—Chemical or biological purification of waste gases of engine exhaust gases
- B01D53/94—Chemical or biological purification of waste gases of engine exhaust gases by catalytic processes
- B01D53/9481—Catalyst preceded by an adsorption device without catalytic function for temporary storage of contaminants, e.g. during cold start
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/92—Chemical or biological purification of waste gases of engine exhaust gases
- B01D53/94—Chemical or biological purification of waste gases of engine exhaust gases by catalytic processes
- B01D53/9481—Catalyst preceded by an adsorption device without catalytic function for temporary storage of contaminants, e.g. during cold start
- B01D53/949—Catalyst preceded by an adsorption device without catalytic function for temporary storage of contaminants, e.g. during cold start for storing sulfur oxides
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/92—Chemical or biological purification of waste gases of engine exhaust gases
- B01D53/94—Chemical or biological purification of waste gases of engine exhaust gases by catalytic processes
- B01D53/9495—Controlling the catalytic process
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F01—MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
- F01N—GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL COMBUSTION ENGINES
- F01N3/00—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust
- F01N3/08—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous
- F01N3/0807—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by using absorbents or adsorbents
- F01N3/0814—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by using absorbents or adsorbents combined with catalytic converters, e.g. NOx absorption/storage reduction catalysts
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F01—MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
- F01N—GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL COMBUSTION ENGINES
- F01N3/00—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust
- F01N3/08—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous
- F01N3/0807—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by using absorbents or adsorbents
- F01N3/0828—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by using absorbents or adsorbents characterised by the absorbed or adsorbed substances
- F01N3/0842—Nitrogen oxides
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F01—MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
- F01N—GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL COMBUSTION ENGINES
- F01N3/00—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust
- F01N3/08—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous
- F01N3/0807—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by using absorbents or adsorbents
- F01N3/0828—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by using absorbents or adsorbents characterised by the absorbed or adsorbed substances
- F01N3/0864—Oxygen
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F01—MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
- F01N—GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL COMBUSTION ENGINES
- F01N3/00—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust
- F01N3/08—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous
- F01N3/0807—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by using absorbents or adsorbents
- F01N3/0871—Regulation of absorbents or adsorbents, e.g. purging
- F01N3/0885—Regeneration of deteriorated absorbents or adsorbents, e.g. desulfurization of NOx traps
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F02—COMBUSTION ENGINES; HOT-GAS OR COMBUSTION-PRODUCT ENGINE PLANTS
- F02D—CONTROLLING COMBUSTION ENGINES
- F02D41/00—Electrical control of supply of combustible mixture or its constituents
- F02D41/02—Circuit arrangements for generating control signals
- F02D41/021—Introducing corrections for particular conditions exterior to the engine
- F02D41/0235—Introducing corrections for particular conditions exterior to the engine in relation with the state of the exhaust gas treating apparatus
- F02D41/027—Introducing corrections for particular conditions exterior to the engine in relation with the state of the exhaust gas treating apparatus to purge or regenerate the exhaust gas treating apparatus
- F02D41/0275—Introducing corrections for particular conditions exterior to the engine in relation with the state of the exhaust gas treating apparatus to purge or regenerate the exhaust gas treating apparatus the exhaust gas treating apparatus being a NOx trap or adsorbent
- F02D41/028—Desulfurisation of NOx traps or adsorbent
Definitions
- the present invention relates to the exhaust gas purification of lean-burn engines.
- the invention relates to a method for desulfating a nitrogen oxide storage catalyst that is a component of an exhaust gas purification system of a lean-burn engine.
- Lean-burn engines are operated primarily with a lean air/fuel mixture, i.e., the air/fuel mixture contains more oxygen than is necessary for complete combustion of the fuel.
- the composition of the air/fuel mixture is frequently described by the air/fuel ratio ⁇ normalized to stoichiometric conditions, hereinafter also referred to as the excess air coefficient.
- the air/fuel ratio for stoichiometric conditions has a value of 14.7 for conventional engine fuels.
- the excess air coefficient in this case is 1.0.
- ⁇ is less than 1.0
- air excess i.e., in a lean air/fuel mixture
- the exhaust gas leaving the engine has the same excess air coefficient as the air/fuel mixture supplied to the engine.
- Lean-burn engines are distinguished by lower fuel consumption as compared to conventional engines, which are operated primarily with a stoichiometric air/fuel mixture.
- Lean-burn engines include gasoline engines developed for lean-burn operation and diesel engines.
- nitrogen oxides storage catalysts adsorb the nitrogen oxides in the lean exhaust gas in the form of nitrates and release them again in rich exhaust gas.
- the mode of operation and composition of nitrogen oxides storage catalysts is described, for example, in European Patent EP 0 560 991 B1.
- the storage material used in these catalysts contains at least one component selected from the group consisting of the alkali metals (potassium, sodium, lithium, cesium), the alkaline-earth metals (barium, calcium) or the rare-earth metals (lanthanum, yttrium).
- the storage catalyst contains platinum as the catalytically active element. Under oxidizing exhaust gas conditions, i.e., in lean-burn operation, the storage materials can store the nitrogen oxides contained in the exhaust gas in the form of nitrates. This requires, however, that the nitrogen oxides, which depending on the engine type and its mode of operation consist of approximately 60 to 95% nitrogen monoxide, are first oxidized to nitrogen dioxide. This occurs on the platinum component of the storage catalyst.
- the catalyst Since the capacity of the storage catalyst is limited, the catalyst must be regenerated from time to time. For this purpose, the excess air coefficient of the air/fuel mixture supplied to the engine, and thus also the excess air coefficient of the exhaust gas leaving the engine, must be lowered briefly to values of less than 1. This is referred to as enriching the air/fuel mixture of the exhaust gas. Thus, during this brief operating phase, reducing conditions are present in the exhaust gas before the exhaust gas enters the storage catalyst.
- the nitrogen oxides stored in the form of nitrates are released again (desorbed) and are reduced to nitrogen on the storage catalyst with simultaneous oxidation of carbon monoxide, hydrocarbons and hydrogen, as in conventional three-way catalysts. This process is hereinafter referred to as NOx regeneration.
- the storage phase typically lasts 60 seconds, while NOx regeneration requires about 5 to 20 seconds.
- nitrogen oxide storage catalysts are not widely used today.
- a significant problem encountered in the use of nitrogen oxide storage catalysts is the sulfur content of the fuels, particularly of diesel fuels.
- Various sulfur compounds are created during combustion—sulfur oxides (SOx) in lean-burn operation.
- SOx sulfur oxides
- the sulfur oxides poison the storage components of the storage catalyst. This poisoning essentially occurs in the same manner as the storage of the nitrogen oxides.
- Sulfur dioxide emitted by the diesel engine is oxidized to sulfur trioxide on the catalytically active noble metal component of the storage catalyst. Sulfur trioxide reacts with the storage materials of the storage catalyst in the presence of the water vapor contained in the exhaust gas to form the corresponding sulfates.
- a particular drawback is that the absorption of sulfur trioxide is preferred compared to the absorption of nitrogen oxides, and the sulfates formed are thermally very stable.
- the formation of the sulfates competes with the storage of the nitrogen oxides (NOx), and the nitrogen oxide storage capacity of the catalyst is clearly reduced because of the poisoning with sulfur oxides. Consequently, the stored sulfur oxides must therefore be removed from the storage catalyst from time to time to restore the full nitrogen oxide storage capacity.
- Removal of sulfur oxides requires special conditions that are distinct from the conditions for NOx regeneration; in other words, during NOx regeneration there is no removal of sulfur components from the storage catalyst, a process hereinafter referred to as desulfation.
- the storage catalyst For desulfation, the storage catalyst must be operated under reducing conditions, i.e., with rich exhaust. In addition, high exhaust gas temperatures are required to heat the catalyst.
- the catalyst temperature required for desulfation depends on the type of storage material used. Typically, the temperatures required for desulfation are above 650° C. This is a critical parameter, since at low temperatures desulfation proceeds too slowly, and at excessively high temperatures the storage catalyst may be permanently damaged by heat.
- German Laid Open Publication DE 198 27 195 A1 describes a method for desulfating a NOx storage catalyst arranged in the exhaust tract of a lean-burn internal combustion engine.
- the internal combustion engine is operated in several rich/lean cycles after a predefined desulfation temperature has been reached.
- the lambda value is reduced to preferably 0.95. This significantly accelerates the emission of the deposited sulfur as sulfur dioxide, while an undesirable hydrogen sulfide formation occurs only with a time delay.
- the duration of the rich phase is selected in such a way that no noticeable emission of hydrogen sulfide is ascertainable.
- the rich and lean periods of the cycles are preferably 2 to 10 seconds and 2 to 6 seconds, respectively.
- German Laid Open Application DE 198 49 082 A1 describes a further method for desulfating a NOx storage catalyst arranged in the exhaust tract of a lean-burn internal combustion engine.
- the lambda value of the exhaust gas is initially reduced to a constant value of about 0.98 for a specific period of time.
- the internal combustion engine is operated with an oscillating lambda value, where the mean value is reduced from 0.98 to a value of 0.93 to 0.95 as a function of time.
- the oscillation frequency is between 0.1 and 0.2 Hz.
- the mean catalyst temperature is increased to approximately 700 to 720° C.
- DE 198 27 195 A1 nor DE 198 49 082 A1 give any indication as to the means used to increase the temperature of the NOx storage catalyst to the desulfation temperature or as to how the temperature is measured. It is feasible, for example, to install a temperature sensor in the body of the NOx storage catalyst. Technically, however, this makes little sense because cracks starting from this installation site and propagating within the body of the NOx storage catalyst because of alternating thermal stresses during operation may eventually destroy the NOx storage catalyst.
- German Laid Open Publication DE 100 26 762 A1 describes a further method for desulfating a NOx storage catalyst.
- a thermocouple for measuring the temperature and a ⁇ /NOx sensor are respectively disposed in the exhaust track.
- the system checks whether SOx regeneration is required by using a suitable mathematical model, a comparison of the lambda signals of a broadband sensor after the NOx storage catalyst during performance, a comparison of the lambda signal before and after the catalyst during NOx regeneration, or the signal of a NOx sensor during the lean phase. If it is determined that SOx regeneration is required, the exhaust temperature is first increased to the desulfation temperature of between 500 and 800° C.
- SOx regeneration is effected by alternating lean/rich operation. The intervals of the alternating lean/rich operation are optionally regulated by constant time periods or by temperature sensors in such a way that the exhaust temperature is maintained within a temperature range optimal for the desulfation process, i.e., between 500 and 800° C.
- DE 100 26 762 A1 proposes additional fuel injection (with and without torque component), late combustion, multistage combustion or external heating means.
- the temperature during desulfation is monitored either by a suitable mathematical model or by temperature sensors disposed upstream and downstream of the storage catalyst.
- Using a mathematical model to regulate the exhaust temperature appears too risky because this does not actually monitor the exhaust temperature so that damage to the catalyst as a result of excessively high exhaust gas temperatures cannot be excluded.
- measuring the temperature upstream of the catalyst provide any information on the actual temperature within the catalyst. Measuring the exhaust temperature downstream of the catalyst is also risky because an excessively high exhaust temperature is detected only after the catalyst has already been damaged.
- the present invention addresses a short-coming of the prior art by providing a method for desulfating a storage catalyst that can be performed with little control complexity and that largely prevents damage to the storage catalyst due to excessively high temperatures during desulfation.
- the present invention provides a method for desulfating a nitrogen oxide storage catalyst that contains stored nitrogen oxides and sulfur oxides and that is a component of an exhaust gas purification system of a lean-burn engine.
- the temperature of the catalyst is increased under lean exhaust conditions to the point at which thermal desorption of the nitrogen oxides stored in the catalyst sets in.
- the onset of thermal desorption of the nitrogen oxides is used as the signal to enrich the air/fuel mixture to perform the desulfation.
- Suitable storage components are oxidic compounds of at least one component of the group consisting of the alkali metals (potassium, sodium, lithium, cesium), the alkaline earth metals (magnesium, barium, calcium, strontium) and the rare earth metals (cerium, lanthanum, yttrium).
- the catalytically active element contained in the storage catalyst is preferably platinum. These materials are capable of adsorbing the nitrogen oxides in the exhaust gas of the lean-burn engine. Depending on the material selected, this adsorption occurs in a temperature range of between 300 and 500° C.
- the present invention provides a method for desulfating a nitrogen oxide storage catalyst, wherein said nitrogen oxide storage catalyst contains stored nitrogen oxides and sulfur oxides and is a component of an exhaust gas purification system of a lean-burn engine, said method comprising: increasing the temperature of a catalyst under lean exhaust conditions to a temperature at which thermal desorption of the nitrogen oxides sets in; and enriching the air/fuel mixture, wherein said enriching is commenced at the onset of said thermal desorption, and said thermal desorption serves as a signal to commence said enriching thereby desulfating of the nitrogen oxide storage catalyst.
- the present invention is directed to a method for desulfating a nitrogen oxides storage catalyst.
- the method commences with NO x regeneration.
- NO x regeneration within the scope of this invention is defined as the release of the adsorbed nitrogen oxides under reducing conditions.
- the reducing conditions are adjusted by enriching the air/fuel mixture to excess air coefficients of between 0.9 and 0.99.
- the nitrogen oxides are then desorbed without requiring any significant temperature increase in the storage catalyst.
- NOx regeneration essentially occurs in the same temperature interval in which adsorption takes place under lean exhaust conditions.
- Experience has shown that NOx regeneration of the storage catalyst is necessary approximately every 1 to 2 minutes.
- the nitrogen oxides can also be released under lean exhaust conditions by a corresponding increase in the temperature.
- this is referred to as thermal desorption of the nitrogen oxides.
- the temperatures required for thermal desorption are typically about 50 to 300° C. above the temperature range where adsorption takes place.
- a decision process which does not form part of the scope of the invention, is used to determine whether desulfation is necessary to restore the nitrogen oxide storage capacity of the storage catalyst. This decision can be made in different ways as described, for example, in DE 100 26 762 A1.
- the concentration of sulfur oxides in the exhaust of a diesel engine is substantially lower than the concentration of nitrogen oxides.
- Desulfation of the storage catalyst is thus required less often than NOx regeneration of the catalyst.
- desulfation may be carried out, for example, at fixed distance intervals, after a predefined number of NOx regenerations or after consumption of a predefined amount of fuel.
- the temperature of the catalyst is increased during a phase when the lean-burn engine is operated with a lean air/fuel mixture, i.e., during a phase when nitrogen oxides are stored on the storage catalyst, until thermal desorption of the nitrogen oxides sets in. Since the exhaust at that moment is lean—unlike in normal NOx regeneration—the desorbed nitrogen oxides leave the storage catalyst without reduction and can be detected using, for example, a nitrogen oxide sensor, which is disposed downstream of the catalyst in the exhaust gas purification system. The onset of the thermal desorption of the nitrogen oxides is used as the signal that the temperature of the storage catalyst has reached a level sufficient for desulfation and that desulfation can be initiated by enriching the exhaust gas.
- Desulfation itself can then be carried out using a conventional method known in the art, preferably using alternating lean/rich operation with suitable amplitudes and frequencies.
- the measures required to increase the temperature are preferably introduced only toward the end of a storage phase for the nitrogen oxides, so as to ensure a defined state of loading with nitrogen oxides of the storage catalyst.
- the temperature increase of the storage catalyst required for desulfation can be achieved by external heating means or by heating the exhaust gas using engine-related measures.
- engine-related measures for external heating of the catalyst, electrical heating of the storage catalyst may be used.
- engine-related measures to heat the exhaust gas in modern diesel engines include additional fuel injection, late combustion or multistage combustion.
- the duration of desulfation is limited to 1 to 20 seconds, preferably 1 to 15 seconds, particularly preferably 2 to 10 seconds. Desulfation is therefore pulsed.
- the optimum duration of the desulfation pulse depends on the following considerations. Unlike in NOx regeneration, it is not desirable in desulfation to reduce the desorbed sulfur oxides. Rather, the sulfur stored on the catalyst should be released into the environment as fully as possible in the form of sulfur dioxide. The reduction of the sulfur oxides causes hydrogen sulfide to form, which is significantly more toxic than sulfur dioxide. The formation of hydrogen sulfide is largely suppressed by the oxygen stored in the exhaust gas purification system during lean-burn operation of the diesel engine.
- the excess air coefficient of the air/fuel mixture supplied to the diesel engine can be modulated during desulfation between a value of less than 1 and a value of more than 1, preferably at a frequency between 1 and 5 Hz.
- the modulation frequency of this oscillating desulfation is selected in such a way that the oxygen stored in the exhaust gas purification system during the rich phases is used up.
- oxygen is again stored in the exhaust gas purification system. This requires a duration of the lean phases between the rich phases of 2 to 15 seconds maximum.
- the lean phases may not be too short because the oxygen storage capacities in the exhaust gas purification system will otherwise not be sufficiently filled. This increases the risk of sulfur emission in the form of hydrogen sulfide and carbonyl sulfide (COS).
- the optimum duration of the lean phases depends on the amount of the oxygen storing components contained in the exhaust gas purification system, on the type of the material, the temperature of the storage catalyst, and the length of the subsequent rich phases. Experience has shown that lean phases in excess of 15 seconds cause the catalyst temperature to drop so that the catalyst needs to be reheated.
- the optimum parameters for the two described desulfation strategies depend on the oxygen storage capacity in the exhaust gas purification system. As a result, they can be influenced through the oxygen storing components with which the storage catalyst is equipped. Preferably, cerium-oxide based oxygen storing components are added to the storage catalyst.
- Desulfation increases fuel consumption because of the required high catalyst temperatures and the necessary enrichment of the air/fuel mixture. This additional fuel consumption can be kept low if desulfation is carried out only during the phases when the diesel engine operates at high load and at correspondingly high exhaust temperatures. In this case, only a slight temperature increase, or even no further temperature increase at all, is required for desulfation.
- a nitrogen oxide sensor also senses sudden oxygen variations and can therefore be used to regulate the air/fuel mixture.
- an oxygen sensor can also be arranged in the exhaust gas purification system upstream of the storage catalyst.
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- Engineering & Computer Science (AREA)
- Chemical & Material Sciences (AREA)
- Combustion & Propulsion (AREA)
- General Engineering & Computer Science (AREA)
- Mechanical Engineering (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Health & Medical Sciences (AREA)
- Environmental & Geological Engineering (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- General Chemical & Material Sciences (AREA)
- Analytical Chemistry (AREA)
- Biomedical Technology (AREA)
- Materials Engineering (AREA)
- Emergency Medicine (AREA)
- Toxicology (AREA)
- Exhaust Gas After Treatment (AREA)
- Exhaust Gas Treatment By Means Of Catalyst (AREA)
- Electrical Control Of Air Or Fuel Supplied To Internal-Combustion Engine (AREA)
- Combined Controls Of Internal Combustion Engines (AREA)
- Catalysts (AREA)
Applications Claiming Priority (3)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
DE10238771A DE10238771B4 (de) | 2002-08-23 | 2002-08-23 | Verfahren zur Desulfatisierung eines Stickoxid-Speicherkatalysators |
DE10238771.0 | 2002-08-23 | ||
DE10238771 | 2002-08-23 |
Publications (2)
Publication Number | Publication Date |
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US20040112042A1 US20040112042A1 (en) | 2004-06-17 |
US6973775B2 true US6973775B2 (en) | 2005-12-13 |
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US10/637,884 Expired - Lifetime US6973775B2 (en) | 2002-08-23 | 2003-08-08 | Method for desulfating a nitrogen oxide storage catalyst |
Country Status (7)
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US (1) | US6973775B2 (de) |
EP (1) | EP1391600B1 (de) |
JP (1) | JP4171681B2 (de) |
KR (1) | KR100959839B1 (de) |
BR (1) | BR0303413B1 (de) |
CA (1) | CA2437069C (de) |
DE (2) | DE10238771B4 (de) |
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US7063642B1 (en) * | 2005-10-07 | 2006-06-20 | Eaton Corporation | Narrow speed range diesel-powered engine system w/ aftertreatment devices |
US20070056268A1 (en) * | 2005-09-10 | 2007-03-15 | Eaton Corporation | LNT-SCR packaging |
US20080028749A1 (en) * | 2006-08-01 | 2008-02-07 | Honda Motor Co., Ltd. | Sulfur purge control device for an internal combustion engine |
US20080276597A1 (en) * | 2005-03-18 | 2008-11-13 | Yasuaki Nakano | Exhaust Gas Purification System for an Internal Combustion Engine |
US20110209459A1 (en) * | 2010-02-26 | 2011-09-01 | Dan Hancu | System and Method for Controlling Nitrous Oxide Emissions of an Internal Combustion Engine and Regeneration of an Exhaust Treatment Device |
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JP3876874B2 (ja) * | 2003-10-28 | 2007-02-07 | トヨタ自動車株式会社 | 触媒再生方法 |
JP4349119B2 (ja) * | 2003-12-19 | 2009-10-21 | いすゞ自動車株式会社 | 排気ガス浄化方法及び排気ガス浄化システム |
US7213395B2 (en) * | 2004-07-14 | 2007-05-08 | Eaton Corporation | Hybrid catalyst system for exhaust emissions reduction |
WO2006041545A2 (en) * | 2004-10-04 | 2006-04-20 | Southwest Research Institute | Method for the simultaneous desulfation of a lean nox trap and regeneration of a diesel particulate filter |
US7849678B2 (en) * | 2005-12-02 | 2010-12-14 | Eaton Corporation | Desulfation control strategy |
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US8209960B2 (en) * | 2006-07-21 | 2012-07-03 | International Engine Intellectual Property Company, Llc | System and method for coupled DPF regeneration and LNT DeNOx |
US20080016851A1 (en) * | 2006-07-21 | 2008-01-24 | Eaton Corporation | System to reduce engine exhaust oxygen using exhaust hydrocarbons and a catalyst positioned upstream of a fuel reformer-LNT system |
US20080072575A1 (en) * | 2006-09-21 | 2008-03-27 | Eaton Corporation | Catalyst to improve low temperature deNOx activity in a reformer-LNT exhaust aftertreatment system |
GB2502832A (en) * | 2012-06-06 | 2013-12-11 | Gm Global Tech Operations Inc | Controlling a Desuiphation Process of a Lean NOx trap |
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DE102014014636A1 (de) | 2014-10-01 | 2016-04-07 | Man Diesel & Turbo Se | Verfahren und Steuerungseinrichtung zum Betreiben eines Systems aus mehreren Brennkraftmaschinen |
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- 2003-08-12 CA CA2437069A patent/CA2437069C/en not_active Expired - Fee Related
- 2003-08-19 EP EP03018624A patent/EP1391600B1/de not_active Expired - Lifetime
- 2003-08-19 DE DE50305883T patent/DE50305883D1/de not_active Expired - Lifetime
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Cited By (10)
Publication number | Priority date | Publication date | Assignee | Title |
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US20050109021A1 (en) * | 2003-11-24 | 2005-05-26 | Remi Noirot | Method and device intended for desulfation of a nitric oxide trap and regeneration of a particle filter |
US7918082B2 (en) * | 2003-11-24 | 2011-04-05 | Institut Francais Du Petrole | Method and device intended for desulfation of a nitric oxide trap and regeneration of a particle filter |
US20080276597A1 (en) * | 2005-03-18 | 2008-11-13 | Yasuaki Nakano | Exhaust Gas Purification System for an Internal Combustion Engine |
US8151554B2 (en) * | 2005-03-18 | 2012-04-10 | Toyota Jidosha Kabushiki Kaisha | Exhaust gas purification system for an internal combustion engine |
US20070056268A1 (en) * | 2005-09-10 | 2007-03-15 | Eaton Corporation | LNT-SCR packaging |
US7063642B1 (en) * | 2005-10-07 | 2006-06-20 | Eaton Corporation | Narrow speed range diesel-powered engine system w/ aftertreatment devices |
US20080028749A1 (en) * | 2006-08-01 | 2008-02-07 | Honda Motor Co., Ltd. | Sulfur purge control device for an internal combustion engine |
US8028518B2 (en) * | 2006-08-01 | 2011-10-04 | Honda Motor Co., Ltd. | Sulfur purge control device for an internal combustion engine |
US20110209459A1 (en) * | 2010-02-26 | 2011-09-01 | Dan Hancu | System and Method for Controlling Nitrous Oxide Emissions of an Internal Combustion Engine and Regeneration of an Exhaust Treatment Device |
US8459010B2 (en) | 2010-02-26 | 2013-06-11 | General Electric Company | System and method for controlling nitrous oxide emissions of an internal combustion engine and regeneration of an exhaust treatment device |
Also Published As
Publication number | Publication date |
---|---|
DE50305883D1 (de) | 2007-01-18 |
CA2437069A1 (en) | 2004-02-23 |
US20040112042A1 (en) | 2004-06-17 |
DE10238771A1 (de) | 2004-03-04 |
BR0303413A (pt) | 2004-09-08 |
JP4171681B2 (ja) | 2008-10-22 |
KR100959839B1 (ko) | 2010-05-28 |
BR0303413B1 (pt) | 2012-11-27 |
EP1391600A1 (de) | 2004-02-25 |
KR20040018228A (ko) | 2004-03-02 |
DE10238771B4 (de) | 2009-01-22 |
CA2437069C (en) | 2011-04-26 |
EP1391600B1 (de) | 2006-12-06 |
JP2004084665A (ja) | 2004-03-18 |
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